Science - 31 January 2020

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SCIENCE sciencemag.org 31 JANUARY 2020 • VOL 367 ISSUE 6477 515

GRAPHIC: X. LIU/S


CIENCE


for private-sector natural capital account-
ing, for example, with the Natural Capital
Protocol. This allows businesses to better
understand their impacts and dependency
on natural capital.

CHALLENGES AND OPPORTUNITIES
Ecosystem accounts published to date vary
in scope and level of (spatial) detail. This re-
flects differences in budget, technical capac-
ity, and data between countries, with notable
constraints in developing countries. Compil-
ing the full suite of ecosystem accounts re-
quires substantial data and use of multiple
biophysical models (see SM, section 2). The
Netherlands ecosystem accounts provide 90
policy-relevant indicators, derived from vari-
ous datasets and models. They indicate, for
example, how small landscape elements such
as hedgerows contribute to crop production
by maintaining pollinator populations.
Institutional challenges occur, for instance,
in relation to integrating data from different
agencies: Data may be in incompatible for-
mats, or there may be a reluctance to share
it. Furthermore, the SEEA has a different
measurement approach compared with some
existing reporting systems (for example,
carbon reporting under the UN Framework
Convention on Climate Change). Collabora-
tion between government institutes holding
different datasets facilitates enhanced data
integration and greater commonality in ter-
minology and definitions ( 13 ).
Some technical challenges remain. For
instance, the diversity of ecosystems makes

selection of ecosystem condition and bio-
diversity indicators challenging. In South
African and Australian accounts, ecosystem
condition has been defined in relation to pre-
European settlement conditions, which is not
useful for western Europe with its long eco-
system-use history. Challenges also exist in
valuing nonmarket ecosystem services such
as water regulation and air filtration.
The EEA’s inherent limitations should be
considered when the accounts are used in
policy-making. The EEA accounts produced
to date do not include indicators for ecosys-
tem resilience or consider probabilities of
sudden future collapses of overexploited eco-
systems ( 15 ). Furthermore, exchange prices
of ecosystem services reflect current pricing
mechanisms and market conditions. Given
that the SEEA does not record the welfare
generated by using natural capital ( 2 ), it is
imperative that monetary values in the EEA
are not interpreted as representing “the value
of nature” (see SM, section 3).
Several ongoing efforts address remain-
ing challenges to the global implementation
of the EEA. The UNSC is working with sci-
entists and statisticians toward establishing
a statistical standard for the EEA by 2021.
Working groups have been established to
address remaining technical issues, includ-
ing defining metrics expressing ecosystem
condition, biodiversity, and the capacity of
ecosystems to supply services and valuing
nonmarket ecosystem services (for instance,
on the basis of simulated exchange values).
Through various scientific efforts connected

to the EEA, such as the Earth Observation for
Ecosystem Accounting initiative of the Group
on Earth Observations, tests are being done
to examine how ecosystem extent, condi-
tion, and regulating services can be modeled
across large countries or even continents at
high resolution using data from remote-
sensing and global datasets. Increasingly,
machine-learning techniques are used, for
instance, to assess the impacts of ecosystem
changes on hydrological cycles and the avail-
ability of water for people. Social media posts
can be used to analyze recreation in ecosys-
tems, for example. The EEA is making large
datasets available to a variety of users, and
global, high-resolution modeling of critical
ecosystem characteristics and services will
facilitate easier uptake of the EEA in develop-
ing countries.
The EEA allows consistent (over time and
between countries), comprehensive, and
high-resolution analysis and reporting on
ecosystems and their use. The EEA accounts
do not capture all connections between peo-
ple and nature and have limited capacity to
consider ecosystem complexities such as
thresholds and feedbacks. These caveats need
to be clearly articulated when EEA accounts
are published. Nonetheless, the EEA consid-
erably enhances the scope and accuracy of in-
formation available in support of ecosystem
management, facilitating better management
of global natural capital. j
REFERENCES AND NOTES


  1. J. Stiglitz, J. Fitoussi, M. Duran, Beyond GDP: Measuring
    What Counts for Economic and Social Performance (OECD
    Publishing, 2018).

  2. D. W. Jorgenson, J. Econ. Lit. 56 , 867 (2018).

  3. UN et al., The System of National Accounts, 2008 (UN,
    2009).

  4. UN et al., “System of environmental-economic account-
    ing 2012: Central framework” (UN, 2014).

  5. UN et al., “System of environmental-economic account-
    ing: Experimental ecosystem accounting” (UN, 2014).

  6. UN, “Technical Recommendations in support of the SEEA
    Experimental Ecosystem Accounting” (UN, 2019).

  7. ONS (Office for National Statistics), “UK natural capital
    accounts: 2019” (ONS, 2019).

  8. Horlings et al., “Experimental monetary valuation of eco-
    system services and assets in the Netherlands” (Report,
    Statistics Netherlands and Wageningen University and
    Research, 2019).

  9. H. Keith et al., Nat. Ecol. Evol. 1 , 1683 (2017).

  10. P. Campos et al., Ecol. Econ. 157 , 218 (2019).

  11. J. L. Nel, A. Driver, “National river ecosystem accounts
    for South Africa” (South African National Biodiversity
    Institute, Pretoria, 2015).

  12. S. Vallecillo et al., “Ecosystem services accounting—Part
    II Pilot accounts for crop and timber provision, global
    climate regulation and flood control” (JRC technical
    reports, Publications Office of the European Union, 2019).

  13. G. Bright et al., Oxf. Rev. Econ. Policy 35 , 88 (2019).

  14. Government of the Netherlands, “National Climate
    Agreement” (2019).
    1 5. C. Fo l ke et al., Ecol. Soc. 21 , 41 (2016).
    ACKNOWLEDGMENTS
    The views expressed in this article are those of the authors
    and do not necessarily reflect the policies of the UN or the
    European Union.
    SUPPLEMENTARY MATERIALS
    science.sciencemag.org/content/367/6477/514/suppl/DC1
    10.1126/science.aaz8901


National National and subnational Subnational

Type of ecosystem accounts compiled

Canada

Mexico Guatemala

United States

Costa Rica
Colombia

Peru
Australia

Japan

China

India

Indonesia

Philippines

South Africa Mauritius
Madagascar

Liberia
Rwanda

Uganda

Croatia

Finland

United Kingdom Netherlands Norway

Denmark
Spain

Italy

Countries that have compiled SEEA EEA accounts
Some countries have published all accounts that they have compiled, and others have published only some.
China, Japan, and the United States have compiled accounts but not published them (see supplementary
materials, section 1). The scope and resolution of the accounts vary between countries. The figure presents
a snapshot—countries continue to compile and publish accounts. SEEA, System of Environmental-Economic
Accounting; EEA, Experimental Ecosys tem Accounting.

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